Sri Sai Ram Mandir Project HA 8.13 › uploads › LUS › Environmental › SRI...Aug 14, 2018 ·...

3536 Concours Street, Suite 100 | Ontario, CA 91764

Office: 909-974-4900 | Fax: 909-974-4004

August 14, 2018 JN 168168

Sri Jayaram Foundation Inc.

Contact: Arunasri Reddy

3579 East Foothill Boulevard, #714

Pasadena, California 91107

SUBJECT: Biological Resources Memorandum for the Sri Sai Ram Mandir Project located in the City

of Chino Sphere of Influence, San Bernardino County, California

Dear Mrs. Reddy,

Michael Baker International (Michael Baker) conducted a habitat assessment for the Sri Sai Ram Mandir Project

(Project) located in the City of Chino Sphere of Influence, San Bernardino County, California. Michael Baker

biologists Ashley Spencer and Frances Yau inventoried and evaluated the condition of the habitat within the

project site on August 6, 2018 to characterize existing site conditions and assess the potential occurrence of

special-status1 plant and wildlife species that could pose a constraint to project implementation. This biological

resources memorandum provides an in-depth assessment of the suitability of the on-site habitat to support

burrowing owl (Athene cunicularia), as well as several other special-status plant and wildlife species identified

by the California Department of Fish and Wildlife’s (CDFW) California Natural Diversity Data Base (CNDDB)

and other electronic databases as potentially occurring in the vicinity of the project site.

PROJECT LOCATION

The project site is generally located north of State Route 91, east of State Route 71, south of State Route 60, and

west of Interstate 15 in the City of Chino Sphere of Influence, San Bernardino County, California (refer to

Exhibit 1, Regional Vicinity). The project site is depicted on the Ontario quadrangle of the United States

Geological Survey’s (USGS) 7.5-minute topographic map series in an un-sectioned area of Township 2 south,

Range 8 west (refer to Exhibit 2, Site Vicinity). Specifically, the project site is located north of Riverside Drive,

east of East End Avenue, south of Walnut Avenue, and west of Roswell Avenue (refer to Exhibit 3, Project Site).

1 As used in this report, “special-status” refers to plant and wildlife species that are federally or State listed, proposed, or candidates;

plant species that have been designated a California Native Plant Society (CNPS) Rare Plant Rank; and wildlife species that are

designated by the California Department of Fish and Wildlife (CDFW) as fully protected, species of special concern, or watch list

species.

August 14, 2018

Page 2 of 9

Sri Sai Ram Mandir Project

Biological Resources Memorandum

PROJECT DESCRIPTION

The proposed project consists of the construction of a 10,000 square foot temple and associated infrastructure,

including a parking lot with seventy-six (76) stalls. In addition, project activities will include landscaping and

the installation of paved driveways (refer to Exhibit 4, Project Depiction).

METHODOLOGY

A literature review and records search was conducted to determine which special-status biological resources

have the potential to occur on or within the general vicinity of the project site. In addition to the literature review,

a general habitat assessment or field survey of the project site and surrounding area was conducted. The field

survey was conducted to document existing conditions within the project site and assess the potential for special-

status biological resources to occur.

Literature Review

Prior to conducting the field survey, a literature review and records search was conducted for special-status

biological resources potentially occurring on or within the vicinity of the project site. Previously recorded

occurrences of special-status plant and wildlife species and their proximity to the project site were determined

through a query of the CDFW’s QuickView Tool in the Biogeographic Information and Observation System

(BIOS), CDFW’s CNDDB Rarefind 5 database, the California Native Plant Society (CNPS) Electronic

Inventory of Rare and Endangered Vascular Plants of California, Calflora Database, compendia of special-status

species published by CDFW, and the U.S. Fish and Wildlife Service (USFWS) species listings.

All available reports, survey results, and literature detailing the biological resources previously observed on or

within the vicinity of the project site were reviewed to understand existing site conditions and note the extent of

any disturbances that have occurred on the project site and surrounding area that would otherwise limit the

distribution of special-status biological resources. Standard field guides and texts were reviewed for specific

habitat requirements of special-status and non-special-status biological resources, as well as the following

resources:

• Google Earth Pro historic aerial imagery (1994 – 2017);

• San Bernardino County General Plan;

• United States Department of Agriculture (USDA) Natural Resource Conservation Service (NRCS) Web Soil Survey; and

• USFWS Critical Habitat designations for Threatened and Endangered Species.

The literature review and records search provided a baseline from which to inventory the biological resources

potentially occurring within the project site. Additional recorded occurrences of those species found on or near

the project site were derived from database queries. The CNDDB database was used, in conjunction with ArcGIS

software, to review historical special-status species occurrence data within the vicinity of the project site.

August 14, 2018

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Habitat Assessment and Field Survey

Michael Baker biologists Ashley Spencer and Frances Yau inventoried and evaluated the condition of the habitat

within the project site on August 6, 2018. Plant communities were preliminarily identified on aerial photographs

and visually inspected during the field survey to document their extent within the project site. The plant

communities occurring within the project site were further evaluated for their potential to provide suitable habitat

for special-status plant and wildlife species as well as function as corridors and/or linkages that may support the

movement of wildlife through the area. Special attention was given to any special-status habitats and/or

undeveloped, natural areas, which have a higher potential to support special-status plant and wildlife species.

All plant and wildlife species, including dominant plant species within each plant community, observed during

the field survey were recorded. Plant species were identified by visual characteristics and morphology in the

field. Unusual and less familiar plant species were photographed during the field survey and identified in the

laboratory using taxonomical guides. Wildlife detections were made through observation of scat, trails, tracks,

burrows, nests, and/or visual and aural observation. In addition, site characteristics including soil condition,

topography, hydrology, anthropogenic disturbances, indicator species, condition of on-site plant communities,

and presence of jurisdictional drainage and/or potential wetland features were noted.

EXISTING SITE CONDITIONS

The project site consists of a disturbed, unvegetated lot located southwest of the intersection of Roswell Avenue

and Walnut Avenue. The project site contains evidence of a high level of human disturbance as a result of on-

going weed abatement activities (i.e. disking) and illegal dumping. Areas surrounding the project site primarily

consist of residential land uses. State Route 60 is located directly north of the project site and State Route 71 is

located approximately 1.5 miles to the west. In addition, an active railway runs along the northern boundary of

the project site in a northwest/southeast direction. On-site surface elevation ranges from approximately 751 to

758 feet above mean sea level (msl) and gently slopes to the south. According to the USDA NRCS Custom Soil

Resource Report for San Bernardino County, the project site is underlain by the following soil units: Grangeville

fine sandy loam (Gr); and Hilmar loamy fine sand (Hr) (refer to Exhibit 5, Soils). Refer to Attachment B for

representative photographs taken throughout the project site.

VEGETATION

The project site appeared to have been recently disked and as a result is primarily unvegetated with a few

scattered ruderal/weedy, low-growing plant species (refer to Exhibit 6, Vegetation). Common plant species

observed within and adjacent to the project site included tree of heaven (Ailanthus altissima), annual burrweed

(Ambrosia acanthicarpa), wild oat (Avena fatua), lamb’s quarters (Chenopodium album), Jimsonweed (Datura

wrightii), common sunflower (Helianthus annuus), prickly lettuce (Lactuca serriola), cheeseweed (Malva

parviflora), tree tobacco (Nicotiana glauca), Russian thistle (Salsola tragus), and puncture vine (Tribulus

terrestris). Several ornamental tree species, including date palm (Phoenix sp.) and Mexican fan palm

(Washingtonia robusta), associated with surrounding residential properties were also observed within and along

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the western and southern boundaries of the project site. Refer to Attachment C for a complete list of plant species

observed during the field survey.

WILDLIFE

Plant communities provide foraging habitat, nesting/denning sites, and shelter from adverse weather or

predations. This section provides a general discussion of those wildlife species that were observed during the

field survey or that are expected to occur within the project site based on existing site conditions. The discussion

is to be used a general reference and is limited by the season, time of day, and weather conditions in which the

field survey was conducted. Wildlife detections were based on calls, songs, scat, tracks, burrows, and direct

observation. Refer to Attachment C for a complete list of wildlife species observed during the field survey.

Fish

No fish or hydrogeomorphic features (e.g., creeks, ponds, lakes, reservoirs) with frequent sources of water that

would support populations of fish were observed on or within the vicinity of the project site. Therefore, no fish

are expected to occur and are presumed absent from the project site.

Amphibians

No amphibians or hydrogeomorphic features (e.g., creeks, ponds, lakes, reservoirs) with frequent sources of

water that would support amphibian species were observed on or within the vicinity of the project site. Therefore,

no amphibians are expected to occur and are presumed absent from the project site.

Reptiles

No reptilian species were observed during the field survey. However, the project site and surrounding area have

the potential to support reptilian species that are adapted to a high level of human disturbance. Common reptilian

species expected to occur within the project site include western side-blotched lizard (Uta stansburiana elegans),

San Diego alligator lizard (Elgaria multicarinata webbii), Great Basin fence lizard (Sceloporus occidentalis

longipes), and Great Basin gopher snake (Pituophis catenifer deserticola).

Birds

Bird species detected during the field survey included Anna’s hummingbird (Calypte anna), American crow

(Corvus brachyrhynchos), house finch (Haemorhous mexicanus), barn swallow (Hirundo rustica), California

towhee (Melozone crissalis), northern mockingbird (Mimus polyglottos), house sparrow (Passer domesticus),

American bushtit (Psaltriparus minimus), black phoebe (Sayornis nigricans), common starling (Sturnus

vulgaris), Cassin’s kingbird (Tyrannus vociferans), and mourning dove (Zenaida macroura).

Mammals

The project site provides suitable habitat for a limited number of mammals that are adapted to a high level of

human disturbance associated with on-going weed abatement activities and illegal dumping. However, most

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mammalian species are nocturnal and are difficult to observe during a diurnal field survey. The only mammalian

species observed during the field survey was California ground squirrel (Otospermophilus beecheyi). Other

common mammalian species expected to occur on the project site include opossum (Didelphis virginiana),

Audubon’s cottontail (Sylvilagus audubonii), and raccoon (Procyon lotor).

NESTING BIRDS

No active nests or birds displaying nesting behavior were observed during the field survey. Although heavily

disturbed, the ornamental trees and vegetation associated with the project site and surrounding residential

properties provide suitable foraging and limited amount of nesting opportunities for a variety of year-round and

seasonal avian residents, as well as migrating songbirds that could occur in the area. Additionally, the project

site provides limited ground nesting opportunities due to the high level of weed abatement activities which would

likely deter birds from nesting on the open ground.

MIGRATORY CORRIDORS AND LINKAGES

Habitat linkages provide links between larger undeveloped habitat areas that are separated by development.

Wildlife corridors are similar to linkages but provide specific opportunities for animals to disperse or migrate

between areas. A corridor can be defined as a linear landscape feature of sufficient width to allow animal

movement between two comparatively undisturbed habitat fragments. Adequate cover is essential for a corridor

to function as a wildlife movement area. It is possible for a habitat corridor to be adequate for one species, but

inadequate for others. Wildlife corridors are significant features for dispersal, seasonal migration, breeding, and

foraging. Additionally, open space can provide a buffer against both human disturbance and natural fluctuations

in resources.

The project site is located in a heavily developed area within Unincorporated San Bernardino County and is

exposed to on-going weed abatement activities (i.e., disking) which limits wildlife movement opportunities

throughout the area. Further, the project site is surrounded by development and light and noise associated with

State Route 60 to the north, the active railway to the east, and the surrounding residential properties to the south,

east, and west would likely deter wildlife from utilizing the project site as a movement corridor. As such,

development of the project site is not expected to disrupt wildlife movement opportunities within or adjacent to

the project site.

JURISDICTIONAL AREAS

There are three key agencies that regulate activities within inland streams, wetlands, and riparian areas in

California. The U.S. Army Corps of Engineers (Corps) Regulatory Branch regulates the discharge of dredge or

fill materials into “waters of the United States” pursuant to Section 404 of the Federal Clean Water Act (CWA),

Section 10 of the Rivers and Harbors Act, and Section 103 of the Marine Protection, Research and Sanctuaries

Act. Of the State agencies, the Regional Water Quality Control Board (Regional Board) regulates discharges to

surface waters pursuant to Section 401 of the CWA and the California Porter-Cologne Water Quality Control

August 14, 2018

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Act, and the CDFW regulates alterations to streambed and associated plant communities under California Fish

and Game Code Sections 1600 et seq. of the California Fish and Game Code.

No jurisdictional drainage and/or wetland features occur within the boundaries of the project site. Therefore,

development of the project site will not result in impacts to Corps, Regional Board, or CDFW jurisdictional areas

and regulatory approvals will not be required.

SPECIAL-STATUS BIOLOGICAL RESOURCES

The CNDDB was queried for reported locations of special-status plant and wildlife species as well as special-

status natural plant communities in the Ontario USGS 7.5-minute quadrangle. A search of published records of

these species was conducted within these quadrangles using the CDFW’s CNDDB Rarefind 5 database and

CNDDB Quickview Tool in BIOS. The habitat assessment evaluated the conditions of the habitat(s) within the

boundaries of the project site to determine if the existing plant communities, at the time of the survey, have the

potential to provide suitable habitat(s) for special-status plant and wildlife species.

The literature search identified seventeen (17) special-status plant species, thirty-four (34) special-status wildlife

species, and one (1) special-status plant community as having the potential to occur within the Ontario USGS

7.5-minute quadrangle. Special-status plant and wildlife species were evaluated for their potential to occur within

the project site based on habitat requirements, availability and quality of suitable habitat, and known

distributions. Special-status plant and wildlife species determined to have the potential to occur within the

vicinity of the project site are presented in Attachment D, Potentially Occurring Special-Status Biological

Resources. Attachment D provides a detailed analysis regarding the potential occurrence of special-status plant

and wildlife species within the project site.

Special-Status Plants

Seventeen (17) special-status plant species have been recorded in the CNDDB and CNPS within the Ontario

USGS 7.5-minute quadrangle (refer to Attachment D). No special-status plant species were observed on-site

during the field survey. The project site is routinely exposed to on-going weed abatement activities (i.e., disking)

and illegal dumping resulting in heavily disturbed soils and an absence of natural plant communities. Therefore,

no special-status plant species are expected to occur and are presumed to be absent from the project site. Focused

surveys for special-status plant species are not recommended.

Special-Status Wildlife

Thirty-four (34) special-status wildlife species have been recorded by the CNDDB within the Ontario USGS

7.5-minute quadrangle (refer to Attachment D). No special-status wildlife species observed during the field

survey. Based on habitat requirements for specific special-status wildlife species and the availability and quality

of habitats needed by each species, it was determined that the project site has a low potential to support Cooper’s

hawk (Accipiter cooperii). All remaining special-status wildlife species are presumed to be absent from the

project site based on habitat requirements, availability and quality of habitat needed by each species, and known

distributions. The potential occurrence of burrowing owl is described in further detail below.

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Burrowing Owl

The burrowing owl is currently listed as a California Species of Special Concern. It is a grassland specialist

distributed throughout western North America where it occupies open areas with short vegetation and bare

ground within shrub, desert, and grassland environments. Burrowing owls use a wide variety of arid and semi-

arid environments with well-drained, level to gently-sloping areas characterized by sparse vegetation and bare

ground (Haug and Didiuk 1993; Dechant et al. 1999). Burrowing owls are dependent upon the presence of

burrowing mammals (such as ground squirrels) whose burrows are used for roosting and nesting (Haug and

Didiuk 1993). The presence or absence of colonial mammal burrows is often a major factor that limits the

presence or absence of burrowing owls. Where mammal burrows are scarce, burrowing owls have been found

occupying man-made cavities, such as buried and non-functioning drain pipes, stand-pipes, and dry culverts.

Burrowing mammals may burrow beneath rocks and debris or large, heavy objects such as abandoned cars,

concrete blocks, or concrete pads. They also require open vegetation allowing line-of-sight observation of the

surrounding habitat to forage as well as watch for predators.

Despite a systematic search of the project site, no burrowing owls or sign of burrowing owl activity (i.e., pellets,

feathers, castings, or white wash) were observed during the field survey. The project site is primarily unvegetated

and/or vegetated with a variety of low-growing plant species that allow for line-of-sight observation favored by

burrowing owls. However, the project site is located within a heavily developed area within Unincorporated San

Bernardino County and is exposed to a high level of disturbance associated with the active railway to the north

and on-going weed abatement activities which would likely deter burrowing owls from occupying the project

site. In addition, several power poles and ornamental trees surround the project site which further decreases the

likelihood that burrowing owls would occur as these features provide perching opportunities for larger raptor

species (i.e., red-tailed hawk [Buteo jamaicensis]) that prey on burrowing owls. Therefore, burrowing owl is

presumed absent from the project site and focused surveys are not recommended.

Special-Status Plant Communities

According to the CNDDB, one (1) special-status plant community has been reported in the Ontario USGS 7.5-

minute quadrangle: Riversidian Alluvial Fan Sage Scrub. Based on the results of the field survey, this special-

status plant community does not occur within the project site.

CRITICAL HABITAT

Critical Habitat refers to specific areas within the geographical range of a species at the time it is listed that

include the physical or biological features that are essential to the survival and eventual recovery of that species.

Maintenance of these physical and biological features requires special management considerations or protection,

regardless of whether individuals or the species are present or not. In the event that a project may result in take

or adverse modification to a species’ designated Critical Habitat, a project proponent may be required to engage

in suitable mitigation. However, consultation for impacts to Critical Habitat is only required when a project has

a federal nexus. This may include projects that occur on federal lands, require federal permits (e.g., CWA Section

August 14, 2018

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404 permit), or receive any federal oversight or funding. If there is a federal nexus, then the federal agency that

is responsible for providing funds or permits would be consult with the USFWS.

The project site is not located within federally designated Critical Habitat. Therefore, impacts to Critical Habitat

will not occur and consultation with the USFWS will not be required for the loss or adverse modification to

Critical Habitat.

CONCLUSION AND RECOMMENDATIONS

The project site primarily consists of a disturbed, unvegetated lot with a few scattered, low-growing plant species

located southwest of the intersection of Roswell Avenue and Walnut Avenue. The project site is routinely

exposed to on-going weed abatement activities (i.e., disking) and illegal dumping resulting in heavily disturbed

soils and an absence of natural plant communities. Therefore, no special-status plant species are expected to

occur within the project site and no additional surveys are recommended.

No special-status wildlife species were observed during the field survey. Based on habitat requirements for

specific special-status wildlife species and the availability and quality of habitats needed by each species, it was

determined that the project site has a low potential to support Cooper’s hawk. All remaining special-status

wildlife species are presumed to be absent from the project site based on habitat requirements, availability and

quality of habitat needed by each species, and known distributions.

Nesting birds are protected pursuant to the Migratory Bird Treaty Act (MBTA) and Sections 3503, 3503.3, 3511,

and 3513 of the California Fish and Game Code. If project activities are to be initiated during the nesting season

(February 1 to August 31), a pre-construction nesting bird clearance survey shall be conducted by a qualified

biologist no more than three (3) days prior to the start of any vegetation removal or ground disturbing activities

to ensure that birds protected under the MBTA and California Fish and Game Code are not impacted. A qualified

biologist shall survey all suitable nesting habitat within the project site, and within a biologically defensible

buffer distance surrounding the project site, for nesting birds prior to commencing project activities.

Documentation of surveys and findings shall be submitted to Sri Jayaram Foundation Inc. for review and file. If

no active nests are detected, construction may begin. If an active nest is found, the bird shall be identified to

species and the approximate distance from the closest work site to the nest shall be estimated and the qualified

biologist shall establish a “no-disturbance” buffer around the active nest. The distance of the “no-disturbance”

buffer may be increased or decreased according to the judgement of the qualified biologist depending on the

level of activity and species (i.e., listed, sensitive). The qualified biologist shall periodically monitor any active

nests to determine if project-related activities occurring outside the ‘no disturbance” buffer disturb the birds and

if the buffer should be increased. Once the young have fledged and left the nest, or the nest otherwise becomes

inactive under natural conditions, construction activities within the buffer area can occur.

Although burrowing owl focused surveys are not recommended, a pre-construction burrowing owl clearance

survey shall be conducted to ensure that burrowing owls remain absent from the project site and impacts to any

occupied burrows do not occur. In accordance with the Staff Report on Burrowing Owl Mitigation (CDFW 2012),

August 14, 2018

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two pre-construction clearance surveys shall be conducted 14-30 days and 24 hours prior to any vegetation

removal or ground disturbing activities. Documentation of surveys and findings shall be submitted to Sri Jayaram

Foundation Inc. for review and file. If no burrowing owls or occupied burrows are detected, construction may

begin. If an occupied burrow is found within the development footprint during pre-construction clearance

surveys, a burrowing owl exclusion plan will need to be prepared and submitted to CDFW for approval prior to

initiating project activities.

No jurisdictional drainage and/or wetland features were observed within or adjacent to the project site. Therefore,

development of the project site will not result in impacts to Corps, Regional Board, or CDFW jurisdictional areas

and regulatory approvals will not be required.

The project site is not located within federally designated Critical Habitat. Therefore, impacts to Critical Habitat

will not occur and consultation with the USFWS will not be required for the loss or adverse modification to

Critical Habitat.

Please do not hesitate to contact me at (909) 974-4961 or [email protected] or Ashley Spencer at

(909) 974-4962 or [email protected] should you have any questions or require further

information.

Sincerely,

Thomas Millington Ashley Spencer

Biologist Biologist

Natural Resources Natural Resources

Attachments:

A. Project Exhibits

B. Site Photographs

C. Flora and Fauna Compendium

D. Potentially Occurring Special-Status Biological Resources

Attachment A

Project Exhibits

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SRI SAI RAM MANDIR PROJECTBIOLOGICAL RESOURCES MEMORANDUM

Regional VicinityExhibit 1

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Project Depiction

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Soils

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Grangeville Fine Sandy Loam

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Disturbed (4.83 Acres)

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Critical Habitat

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Southwestern Willow Flycatcher (Empidonax traillii extimus)Yellow-Billed Cuckoo (Coccyzus americanus)Least Bell's Vireo (Vireo bellii pusillus)Coastal California Gnatcatcher (Polioptila californica californica)

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Attachment B

Site Photographs

Attachment B – Site Photographs



Photograph 1: Standing within the southeastern portion of the project site looking west. Evidence of

recent weed abatement activities (i.e., disking) can be seen in the foreground.

Photograph 2: Looking northwest across the western portion of the project site. Evidence of illegal

dumping can be seen in the distance.




Photograph 3: Looking southwest across the central portion of the project site.

Photograph 4: Standing within the northern portion of the project site looking southeast across the

project site.




Photograph 5: Standing within the southeastern portion of the project site looking south across the

project site.

Photograph 6: Standing within the southeastern portion of the project site looking northwest.

Attachment C

Flora and Fauna Compendium

Attachment C – Flora and Fauna Compendium



Table C – 1: Plant Species

Scientific Name Common Name

Ailanthus altissima*

Ambrosia acanthicarpa

Avena fatua*

Baccharis salicifolia

Bromus diandrus*

Bromus madritensis ssp. rubens*

Chenopodium album*

Convolvulus arvensis*

Datura wrightii

Digitaria sanguinalis*

Erigeron bonariensis*

Erodium cicutarium*

Euphorbia maculata *

Helianthus annuus

Lactuca serriola*

Malva parviflora*

Nicotiana glauca *

Phoenix sp.*

Pseudognaphalium luteoalbum*

Salix lasiolepis

Salsola tragus*

Schismus barbatus*

Solanum elaeagnifolium*

Tribulus terrestris*

Washingtonia robusta*

tree of heaven

annual burrweed

wild oat

mulefat

ripgut brome

foxtail brome

lamb’s quaters

field bindweed

Jimsonweed

hairy crabgrass

flax-leaved horseweed

coastal heron’s bill

spotted spurge

common sunflower

prickly lettuce

cheeseweed

tree tobacco

date palm

Jersey cudweed

arroyo willow

Russian thistle

common Mediterranean grass

horse nettle

puncture vine

Mexican fan palm

Table C – 2: Wildlife Species

Scientific Name Common Name

Aves Birds

Calypte anna Anna’s hummingbird

Corvus brachyrhynchos

Haemorhous mexicanus

Hirundo rustica

Melozone crissalis

Mimus polyglottos

Passer domesticus

Psaltriparus minimus

Sayornis nigricans

Sturnus vulgaris

Tyrannus vociferans

American crow

house finch

barn swallow

California towhee

northern mockingbird

house sparrow

American bushtit

black phoebe

common starling

Cassin’s kingbird

Zenaida macroura mourning dove

Mammalia Mammals

Otospermophilus beecheyi California ground squirrel

*Non-native/invasive

Attachment D

Potentially Occurring Special-Status Biological Resources

Attachment D – Potentially Occurring Special-Status Biological Resources



Table D-1: Potentially Occurring Special-Status Biological Resources

Scientific Name

Common Name Status Habitat

Observed

Onsite Potential to Occur

SPECIAL-STATUS WILDLIFE SPECIES

Accipiter cooperii

Cooper’s hawk

Fed:

CA:

None

WL

Generally, found in forested areas up to 3,000 feet in elevation,

especially near edges and rivers. Prefers hardwood stands and mature

forests, but can be found in urban and suburban areas where there are tall trees for nesting. Common in open areas during nesting season.

No

Low:

Some suitable foraging habitat is present within the project site.

Additionally, this species is

known to occur within urban areas.

Anniella stebbinsi

southern California legless lizard

Fed:

CA:

None

SSC

Locally abundant specimens are found in coastal sand dunes and a

variety of interior habitats, including sandy washes and alluvial fans.

A large protected population persists in the remnant of the once

extensive El Segundo Dunes at Los Angeles International Airport.

No Presumed Absent:

No suitable habitat is present within the project site.

Antrozous pallidus

pallid bat Fed: CA:

None SSC

Common of low elevations in California. Occupies a variety of

habitats including grasslands, shrublands, woodlands, and forests from sea level up through mixed conifer forests. Most common in open, dry

habitats with rocky areas for roosting.

No

Presumed Absent:

No suitable habitat is present

within the project site.

Arizona elegans occidentalis

California glossy snake

Fed:

CA:

None

SSC Inhabits arid scrub, rocky washes, grasslands, and chaparral habitats. No

Presumed Absent:



Artemisiospiza belli belli

Bell's sage sparrow Fed: CA:

None WL

Occurs in chaparral dominated by fairly dense stands of chamise. Also found in coastal sage scrub in south of range.

No Presumed Absent:


Aspidoscelis tigris stejnegeri

coastal whiptail Fed: CA:

None SSC

Found in a variety of ecosystems, primarily hot and dry open areas with sparse foliage - chaparral, woodland, and riparian areas.

No

Presumed Absent:



Athene cunicularia

burrowing owl

Fed:

CA:

None

SSC

Primarily a grassland species, but it persists and even thrives in some landscapes highly altered by human activity. Occurs in open, annual

or perennial grasslands, deserts, and scrublands characterized by low-

growing vegetation. The overriding characteristics of suitable habitat appear to be burrows for roosting and nesting and relatively short

vegetation with only sparse shrubs and taller vegetation.

No Presumed Absent:


Buteo swainsoni

Swainson's hawk

Fed:

CA:

None

THR

Typical habitat is open desert, grassland, or cropland containing

scattered, large trees or small groves. Breeds in stands with few trees in juniper-sage flats, riparian areas, and in oak savannah in the Central

Valley. Forages in adjacent grassland or suitable grain or alfalfa fields

or livestock pastures.

No

Presumed Absent:



Campylorhynchus brunneicapillus sandiegensis

coastal cactus wren

Fed:

CA:

None

SSC

The coastal population inhabits cactus scrub from southern Ventura

County and southwestern San Bernardino County to northwestern

Baja California. Key habitat element is thickets of chollas or prickly-pear cacti tall enough to support and protect the birds’ nests.

No

Presumed Absent:






Scientific Name


Observed


Chaetodipus fallax fallax

northwestern San Diego pocket mouse Fed: CA:

None SSC

Occurs in desert and coastal habitats in southern California, Mexico, and northern Baja California, from sea level to at least 4,596 feet above

msl. Found in a variety of temperate habitats ranging from chaparral

and grasslands to scrub forests and deserts. Requires low growing vegetation or rocky outcroppings, as well as sandy soils for burrowing.

No

Presumed Absent:



Circus cyaneus

northern harrier

Fed:

CA:

None

SSC

Frequents meadows, grasslands, open rangelands, desert sinks, fresh

and saltwater emergent wetlands; seldom found in wooded areas.

Mostly found in flat, or hummocky, open areas of tall, dense grasses moist or dry shrubs, and edges for nesting, cover, and feeding.

No

Presumed Absent:



Dipodomys merriami parvus

San Bernardino kangaroo rat Fed: CA:

END SSC

Primarily found in Riversidian alluvial fan sage scrub and sandy loam

soils, alluvial fans and flood plains, and along washes with nearby sage scrub. May occur at lower densities in Riversidian upland sage scrub,

chaparral and grassland in uplands and tributaries in proximity to

Riversidian alluvial fan sage scrub habitats. Tend to avoid rocky substrates and prefer sandy loam substrates for digging of shallow

burrows.

No

Presumed Absent:



Emys marmorata

western pond turtle

Fed:

CA:

None

SSC

Found in ponds, lakes, rivers, streams, creeks, marshes, and irrigation

ditches, with abundant vegetation, either rocky or muddy bottoms, in woodland, forest, and grassland. In streams, prefers pools to shallower

areas. Logs, rocks, cattail mats, and exposed banks are required for

basking. May enter brackish water and even seawater. Found at elevations from sea level to over 5,900 feet in elevation.

No

Presumed Absent:



Eumops perotis californicus

western mastiff bat Fed: CA:

None SSC

Primarily a cliff-dwelling species, roost generally under exfoliating

rock slabs. Roosts are generally high above the ground, usually allowing a clear vertical drop of at least three meters below the

entrance for flight. In California, it is most frequently encountered in

broad open areas. Its foraging habitat includes dry desert washes, flood plains, chaparral, oak woodland, open ponderosa pine forest,

grassland, and agricultural areas.

No

Presumed Absent:



Falco columbarius

merlin

Fed:

CA:

None

WL

Nest in forested openings, edges, and along rivers across northern North America. Found in open forests, grasslands, and especially

coastal areas with flocks of small songbirds or shorebirds. Occurs at

elevations below 3,900 feet above msl.

No

Presumed Absent:



Falco mexicanus

prairie falcon

Fed:

CA:

None

WL

Ranges from southeastern deserts northwest throughout the Central Valley and along the inner Coast Ranges and Sierra Nevada.

Distributed from annual grasslands to alpine meadows, but associated

primarily with perennial grasslands, savannahs, rangeland, some agricultural fields, and desert scrub. Within the Sierra Nevada, this

species range above the timberline in late summer, but winter at lower

elevations. During the breeding season, this species is commonly found in foothills and mountains which provide cliffs and escarpments

for nesting.

No

Presumed Absent:






Scientific Name


Observed


Icteria virens

yellow-breasted chat

Fed:

CA:

None

SSC

Primarily found in tall, dense, relatively wide riparian woodlands and thickets of willows, vine tangles, and dense brush with well-developed

understories. Nesting areas are associated with streams, swampy

ground, and the borders of small ponds. Breeding habitat must be dense to provide shade and concealment. It winters south the Central

America. Found at elevations ranging from 820 to 2,625 feet above

msl.

No

Presumed Absent:



Lanius ludovicianus

loggerhead shrike

Fed:

CA:

None

SSC

Often found in broken woodlands, shrublands, and other habitats.

Prefers open country with scattered perches for hunting and fairly dense brush for nesting.

No

Presumed Absent:



Lasiurus xanthinus

western yellow bat

Fed:

CA:

None

SSC

Roosts in palm trees in foothill riparian, desert wash, and palm oasis

habitats with access to water for foraging. No

Presumed Absent:


Laterallus jamaicensis coturniculus

California black rail

Fed:

CA:

None

THR ; FP

Suitable habitat generally includes salt marches, freshwater marshes,

and wet meadows. Typical associated vegetation includes pickle weed

(Salicornia virginica), in salt marshes and bulrush (Scirpus spp.) in less saline habitats.

No

Presumed Absent:



Neotoma lepida intermedia

San Diego desert woodrat Fed: CA:

None SSC

Occurs in coastal scrub communities between San Luis Obispo and

San Diego Counties. Prefers moderate to dense canopies, and

especially rocky outcrops.

No

Presumed Absent:



Nyctinomops macrotis

big free-tailed bat Fed: CA:

None SSC

Maternity roosts have been documented in rock crevices, with

evidence of long term use. Mainly roost in crevices and rocks in cliff situations. Some have been documented roosting in buildings, caves,

and tree cavities.

No

Presumed Absent:



Perognathus longimembris brevinasus

Los Angeles pocket mouse

Fed:

CA:

None

SSC

Occurs in lower elevation grasslands and coastal sage scrub communities in and around the Los Angeles Basin. Prefers open

ground with fine sandy soils. May not dig extensive burrows, but

instead will seek refuge under weeds and dead leaves instead.

No

Presumed Absent:



Phrynosoma blainvillii

coast horned lizard

Fed:

CA:

None

SSC

Occurs in a wide variety of vegetation types including coastal sage

scrub, annual grassland, chaparral, oak woodland, riparian woodland

and coniferous forest. In inland areas, this species is restricted to areas with pockets of open microhabitat, created by disturbance (i.e. fire,

floods, roads, grazing, fire breaks). The key elements of such habitats

are loose, fine soils with a high sand fraction; an abundance of native ants or other insects; and open areas with limited overstory for basking

and low, but relatively dense shrubs for refuge.

No

Presumed Absent:



Polioptila californica californica

coastal California gnatcatcher Fed: CA:

THR SSC

Obligate resident of sage scrub habitats that are dominated by

California sagebrush. This species generally occurs below 750 feet elevation in coastal regions and below 1,500 feet inland. It prefers

habitat with more low-growing vegetation.

No

Presumed Absent:



Rana boylii

foothill yellow-legged frog

Fed:

CA:

None

CTHR ; SSC

Frequents rocky streams and rivers with rocky substrate and open, sunny banks, in forests, chaparral, and woodlands. Sometimes found

in isolated pools, vegetated backwaters, and deep, shaded, spring-fed

pools.

No

Presumed Absent:






Scientific Name


Observed


Rana draytonii

California red-legged frog Fed: CA:

THR SSC

Found mainly near ponds in humid forests, woodlands, grasslands, coastal scrub, and stream sides with plant cover. Most common in

lowlands or foothills. Frequently found in woods adjacent to streams.

Occurs along the coast ranges from Mendocino County south and in portions of the Sierra Nevada and Cascades ranges.

No

Presumed Absent:



Salvadora hexalepis virgultea

coast patch-nosed snake

Fed:

CA:

None

SSC

Inhabits semi-arid brushy areas and chaparral in canyons, rocky

hillsides, and plains. Requires friable soils for burrowing. No

Presumed Absent:



Setophaga petechia

yellow warbler Fed: CA:

None SSC

Nests over all of California except the Central Valley, the Mojave

Desert region, and high altitudes and the eastern side of the Sierra

Nevada. Winters along the Colorado River and in parts of Imperial and Riverside Counties. Nests in riparian areas dominated by willows,

cottonwoods, sycamores, or alders or in mature chaparral. May also

use oaks, conifers, and urban areas near stream courses.

No

Presumed Absent:



Spea hammondii

western spadefoot Fed: CA:

None SSC

Prefers open areas with sandy or gravelly soils, in a variety of habitats including mixed woodlands, grasslands, coastal sage scrub, chaparral,

sandy washed, lowlands, river floodplains, alluvial fans, playas, alkali

flats, foothills, and mountains. Rainpools which do not contain bullfrogs, fish, or crayfish are necessary for breeding.

No

Presumed Absent:



Taricha torosa

Coast Range newt

Fed:

CA:

None

SSC

Found in wet forests, oak forests, chaparral, and rolling grasslands. In southern California, drier chaparral, oak woodland, and grasslands are

used.

No

Presumed Absent:



Thamnophis hammondii

two-striped gartersnake Fed: CA:

None SSC

Utilizes a variety of habitats including forests, mixed woodlands, grassland, chaparral, and farmlands. Often found near ponds, marshes,

or streams. No

Presumed Absent:



Thamnophis sirtalis infernalis

south coast gartersnake Fed: CA:

None SSC

Utilizes a variety of habitats including forests, mixed woodlands,

grassland, chaparral, and farmlands. Often found near ponds, marshes,

or streams.

No

Presumed Absent:



Xanthocephalus xanthocephalus

yellow-headed blackbird Fed: CA:

None SSC

Occurs in freshwater emergent wetlands, and moist, open areas along

croplands and mud flats of lacustrine habitats. Prefers to nest in dense wetland vegetation characterized by tules, cattails, or other similar

plant species along the border of lakes and ponds.

No

Presumed Absent:



SPECIAL-STATUS PLANT SPECIES

Calochortus catalinae

Catalina mariposa-lily

Fed:

CA:

CNPS:

None

None

4.2

Habitats include chaparral, cismontane woodland, coastal scrub,

valley and foothill grassland. Found at elevations ranging from 49 to 2,297 feet above mean sea level (msl). Blooming period is from

February to June.

No

Presumed Absent:



Calochortus plummerae

Plummer's mariposa-lily

Fed: CA:

CNPS:

None None

4.2

Prefers openings in chaparral, foothill woodland, coastal sage scrub, valley foothill grasslands, cismontane woodland, lower montane

coniferous forest and yellow pine forest. Often found on dry, rocky

slopes and soils and brushy areas. Can be very common after a fire. Found at elevations ranging from 459 to 6,299 feet above msl.

Blooming period is from May to July.

No Presumed Absent:





Scientific Name


Observed


Calystegia felix

lucky morning-glory

Fed:

CA: CNPS:

None

None 1B.1

Historically associated with wetland and marshy places, but possibly in drier situations as well. Found in riparian scrub, meadows and seeps.

Found at elevations ranging from 98 to 705 feet above msl. Blooming

period is from March to September.

No

Presumed Absent:



Centromadia pungens ssp. laevis

smooth tarplant

Fed:

CA: CNPS:

None

None 1B.1

Occurs in alkaline soils within chenopod scrub, meadows and seeps, playas, riparian woodland, valley and foothill grassland habitats.

Found at elevations ranging from 0 to 2,100 feet above msl. Blooming

period is from April to September.

No

Presumed Absent:



Chorizanthe parryi var. parryi

Parry's spineflower

Fed: CA:

CNPS:

None None

1B.1

Grows in sandy or rocky openings within chaparral, cismontane

woodland, coastal scrub, and valley and foothill grassland habitats.

Found at elevations ranging from 902 to 4,003 feet above msl. Blooming period is from April to June.

No

Presumed Absent:



Cladium californicum

California saw-grass

Fed: CA:

CNPS:

None None

2B.2

Grows in alkaline or freshwater marshes and swamps. Additionally found in meadows and seeps. Found at elevations ranging from 197 to

2,838 feet above msl. Blooming period is from June to September.

No Presumed Absent:


Dodecahema leptoceras

slender-horned spineflower

Fed: CA:

CNPS:

END END

1B.1

Chaparral, coastal scrub (alluvial fan sage scrub). Flood deposited terraces and washes. Found at elevations ranging from 1,181 to 2,690

feet above msl. Blooming period is from April to June.

No

Presumed Absent:



Horkelia cuneata var. puberula

mesa horkelia

Fed: CA:

CNPS:

None None

1B.1

Open sandy fields and chaparral, mostly away from the coast, old

dunes, foothill edge of LA Basin, south Coast, Peninsular range.

Found at elevations ranging from 230 to 2,657 feet above msl. Blooming period is from February to September.

No Presumed Absent:


Juglans californica

southern California black walnut

Fed:

CA:

CNPS:

None

None

4.2

Found in chaparral, cismontane woodland, coastal scrub, and riparian

woodland habitats. Found at elevations ranging from 164 to 2,953 feet

above msl. Blooming period is from March to August.

No

Presumed Absent:



Juncus acutus ssp. leopoldii

southwestern spiny rush

Fed:

CA: CNPS:

None

None 4.2

Occurs in coastal dunes (mesic), meadows and seeps (alkaline seeps), and marshes and swamps (coastal salt) habitats. Found at elevations

ranging from 9 to 2,953 feet above msl. Blooming period is (March)

May to June.

No

Presumed Absent:



Lepidium virginicum var. robinsonii

Robinson's pepper-grass

Fed:

CA: CNPS:

None

None 4.3

Dry soils on chaparral and coastal sage scrub. Found at elevations

ranging from 3 to 2,904 feet above msl. Blooming period is from January to July.

No

Presumed Absent:



Muhlenbergia californica

California muhly

Fed:

CA: CNPS:

None

None 4.3

Found in chaparral, coastal scrub, lower montane coniferous forest,

meadows and seeps. Found at elevations ranging from 328 to 6,562 feet above msl. Blooming period is from June to September.

No

Presumed Absent:



Navarretia prostrata

prostrate vernal pool navarretia

Fed:

CA: CNPS:

None

None 1B.1

Grows in coastal scrub, vernal pools, meadows and seeps, valley and

foothill grassland habitats. Found at elevations ranging from 10 to 3,970 feet above msl. Blooming period is from April to July.

No

Presumed Absent:



Pseudognaphalium leucocephalum

white rabbit-tobacco

Fed:

CA:

CNPS:

None

None

2B.2

Found in sandy and gravelly soils within chaparral, cismontane woodland, coastal scrub, and riparian woodland habitats. Occurs at

elevations ranging from 0 to 6,890 feet above msl. Blooming period is

from August to November.

No

Presumed Absent:






Scientific Name


Observed


Sidalcea neomexicana

salt spring checkerbloom

Fed:

CA: CNPS:

None

None 2B.2

Habitat includes chaparral, coastal scrub, lower montane coniferous forest, plays, and mojavean desert scrub. Found at elevations ranging

from 49 to 5,020 feet above msl. Blooming period is from March to

June.

No

Presumed Absent:



Symphyotrichum defoliatum

San Bernardino aster

Fed: CA:

CNPS:

None None

1B.2

Grows in cismontane woodland, coastal scrub, lower montane coniferous forest, meadows and seeps, marshes and swamps, valley

and foothill grassland (vernally mesic). Can be found growing near

ditches, streams, and springs within these habitats. Found at elevations ranging from 7 to 6,693 feet above msl. Blooming period is from July

to November.

No

Presumed Absent:



Thysanocarpus rigidus

rigid fringepod

Fed:

CA:

CNPS:

None

None

1B.2

Found in dry, rocky slopes within pinyon and juniper woodland

habitat. Found at elevations ranging from 1,969 to 7,218 feet above

msl. Blooming period is from February to May.

No

Presumed Absent:



SPECIAL-STATUS PLANT COMMUNITIES

Riversidian Alluvial Fan Sage Scrub CDFW Sensitive

Habitat

Occur within broad washes of sandy alluvial drainages that carry rainfall runoff sporadically in winter and spring but remain relatively

dry through the remainder of the year. Is restricted to drainages and

floodplains with very sandy substrates that have a dearth of decomposed plant material. These areas do not develop into riparian

woodland or scrub due to the limited water resources and scouring by

occasional floods.

No

Absent

U.S. Fish and Wildlife Service (USFWS) -

Federal

END - Federal Endangered THR - Federal Threatened

California Department of Fish and Wildlife

(CDFW) - California

END- California Endangered THR - California Threatened

CTHR - The classification provided to a native

species or subspecies of a bird, mammal, fish, amphibian, reptile, or plant that the Fish and

Game Commission has formally noticed as

being under review by the Department of Fish and Wildlife for addition to the list of

threatened species, or a species for which the

commission has published a notice of proposed regulation to add the species to the

list of threatened species.

SSC - California Species of Concern WL - Watch List

FP - California Fully Protected

California Native Plant Society (CNPS)

California Rare Plant Rank

1B Plants Rare, Threatened, or Endangered in California and Elsewhere

2B Plants Rare, Threatened, or Endangered in

California, but More Common Elsewhere 4 Plants of Limited Distribution – A Watch List

Threat Ranks

0.1 - Seriously threatened in California

0.2 - Moderately threatened in California 0.3 - Not very threatened in California

Sri Sai Ram Mandir Project HA 8.13 › uploads › LUS › Environmental › SRI...Aug 14, 2018 ·...

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